Field experiment reveals that site-specific conditions outweigh erosion states in governing nitrogen turnover and emissions in agricultural soils, highlighting the need for localized soil management.
Understanding how nitrogen (N) cycling is affected by soil erosion is essential to optimize N supply for crops and reduce losses in hilly fields. While topography-related impacts on N availability and losses have been studied, the mechanisms linking erosion to N transformation dynamics remain unclear. We conducted a field experiment at two sites to investigate gross N transformation, plant N uptake, and nitrous oxide (N 2 O) emissions from different sources in erosion-affected soils. Two 15 N-labelling approaches were combined: process-based modelling of N transformation following in situ 15 N tracing after fertilization and season-long 15 N balancing, to trace 15 N-enriched fertilizer N in maize biomass, soil and N 2 O emissions. Although differences in gross N transformation rates, N 2 O emissions, crop yields, and total 15 N recovery were more pronounced between sites than between soils, several N measures showed site-specific trends across erosion-affected soils. In Dedelow, gross N mineralization, NH 4 + immobilization, and NH 4 + oxidation were at least twofold higher in eroded compared to non-eroded and deposited soils. This contrasts with the expectation that eroded soils generally exhibit reduced N turnover and the lowest soil fertility. In Friedrichshof, seasonal N 2 O emissions tended to be higher in deposited and eroded soils than non-eroded soils. However, N measures did not follow the same pattern across soils between sites, except for crop yield and soil-derived N supply, both increasing in the order non-eroded < eroded < deposited soils at both sites. Our findings emphasize the importance of temporal and site-specific conditions for managing N supply and losses in erosion-affected soils.
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Schoof et al. (2026) studied this question.
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